Timeline

Table 1: A timeline of research plans and progress.

Background

Positive interactions drive ecosystem infrastructure (R. M. Callaway 1997; Gelmi-Candusso, Heymann, and Heer 2017). A positive interaction is any association between multiple individuals where one or more of the interactors benefits, either in physical health or reproductive fitness (M. D. M. Bertness and Callaway 1994). These interactions are described by the Kingdom-level pathway they follow from benefactor to protegee (e.g. plant-plant, plant-animal, plant-animal-plant, etc.). By analyzing more narrow taxonomic interactions in a variety of ecosystems, we are able to further understand the importance of positive interactions in ecosystem structure and dynamics.

Mutualism, a more specific kind of interspecifc interaction, is when both parties involved benefit from interacting (Barker et al. 2017; Bronstein 2009; Bronstein 2001). In harsh ecosystems (like deserts or islands), we see examples of “double mutualism”, where each interactor exists in two distinct niches to provide two distinct services to an interspecific (Ladley and Kelly 1996; Kelly et al. 2004; Garcia, Espadaler, and Olesen 2012; Gomes, Quirino, and Araujo 2014). Mutualism and double mutualism are most commonly discussed when an animal is an interacting species.

Facilitation, however, usually references positive interactions where a plant is the benefactor species (i.e. plant-plant or plant-animal interactions) (F. T. Maestre et al. 2009). Benefactor plant species increase germination, growth, and recruitment of protegee species existing under its canopy (Franco and Nobel 2009). In arid ecosystems, facilitation takes the form of benefactor species providing resources like water, shade, and pollinators (Flores-Torres and Galindo-Escamilla 2017; Miranda-Jacome, Montaña, and Fornoni 2013; Mitchell et al. 2009), or protection from trauma by herbivory, trampling, freezing temperatures, predation, and wind (Gomez-Aparicio et al. 2008; Parker 1989; Tewksbury and Lloyd 2001; P. S. Nobel 1980). Keystone benefactor species which facilitate many species in an ecosystem are known as foundational species (Angelini et al. 2011; Almeida and Mikich 2018), and are dominant species in a ecosystem. Shrub species have been documented as the most common foundational species globally (Filazzola et al. 2017). Cylindropuntia acanthocarpa, a many-branched columnar member of the Cactaceae family is found as a dominant species in the Mojave Desert. It is morphologically similar to foundational shrubs, and likely is a keystone foundational species itself. Members of the Cactaceae family have been documented as both protegee species and benefactor species in deserts. Carnegiea gigantea, a keystone columnar cactus species found in the Sonoran Desert, was the subject of the classic paper on facilitation, as a protegee species (Turner et al. 1966). It is an obligate protegee in that its seeds must be deposited under a benefactor shrub’s canopy in order to germinate (Taly D. Drezner and Garrity 2003; Taly Dawn Drezner 2010). This dual role as a benefactor and protegee at different life stages makes Cactaceae an interesting player in interaction ecology.

Before a plant can germinate, grow, and eventually facilitate other species, it must first be created (via sexual reproduction) and then disperse from the mother plant as a seed (Nathan and Muller-landau 2000). While clonal reproduction is common in Cylindropuntia species, it is seed dispersal which allows a mother plant to expand its seed shadow over a larger landscape in a shorter period of time (Willson 1993). Seed dispersal can rely on biotic or abiotic vectors, but endozoochorous seed dispersal (dispersal through the gut of an animal) is shown to increase germination rate, especially by birds (Verdu and Traveset 2004; A Traveset, Riera, and Mas 2001; A. Traveset and Verdú 2002).

Birds are known nectarivores and frugivores of cacti (Montiel and Montaña 2000; Gorostiague and Ortega-Baes 2016), and this interaction provides food resources for birds and pollination/seed dispersal for cacti. Should they occur within the same taxonomic groups in one habitat, these interactions may be described as double mutualism. However, nectarivores and frugivores do not forage randomly, but instead follow optimal foraging theory which suggests that foragers will continue to forage in one area until resources are depleted to levels below the average resource availability of the larger habitat. This value resource density is known as the Giving Up Density, or GUD, which exists based on predictions made in ecosystems with patchy resource available (Marginal Value Theorem) (Charnov 1976). This suggests that in a mutualistic foraging interaction, cacti will evolve to have more reproductive output and showier displays to draw in more nectarivores (Wolf and Hainsworth 1990; Mitchell 1994). However, allocation theory suggests that plants must make physiological trade offs due to their finite energy to anatomical traits that best increase their relative fitness (Obeso 2004). Therefore, plants which maximize reproductive output and size will be the most likely to encourage pollinator and frugivorous visitation.

Deserts habitats are declining due to the effects of climate change, fragmentation, and invasive species (Nielsen and Ball 2015; Pfahl, O’Gorman, and Fischer 2017; Singh et al. 2013; Smith 2011; Gutzwiller and Barrow 2003; Hernandez et al. 2014; Rodriguez-Estrella 2007) and the family Cactaceae is protected under CITES Appendix II, with many species protected under Appendix I (CITES 2017). Understanding how cacti come to be dominant species in an ecosystem may illuminate new avenues for utilizing biotic vectors in conservation and restoration applications.

Chapter 1

A meta analysis of physical allocation in Cactaceae reproductive structures

Purpose: Review literature on Cactaceae reproduction outputs, analyze reported values, and determine research gaps and future directions for agro-eco investigations. Produce editorial paper on current state of agro-eco Cactaceae research, as well as a meta analysis paper quantifying reported allocation trade offs of Cactaceae.

Research Questions: Are reproductive outputs in Cactaceae (flowers, fruits, and seeds) correlated? How does Cactaceae phylogenetic distance related to reproductive output? Where are Cactaceae reproductive studies relative to Cactaceae locations? What research gaps exist in Cactaceae allocation research, and what opportunities for argo-eco interdisciplinary work have been unexplored?

Hypothesis: Flower production will be greater than, but correlated to fruit production. However, fruit production will be negatively correlated with seed production. Abundance of fruit or seeds will also be negatively correlated with mass of fruit or seeds, respectively.

Methods: A systematic review using search terms (Table 2) was performed in Web of Science. Screening for a qualitative synthesis versus screening for a quantitative analysis led to one additional study for the qualitative. Since only 14 studies have been identified, the search will be expanded to include “flower*" as a search term, and allow for papers published more than five years ago. A PRISMA statement shows the current exclusion for all studies (Figure 1). Data will be analyzed using the R Package “metafor” with generalized linear mixed models.

Figure 1: A PRISMA statement showing sample size of papers included in qualitative and quantitative datasets.

Table 2: The number of studies returned for each combination of search terms in Web of Science.

Preliminary Results:

This study has changed from its original construct which relied on reports of correlation coefficients between reproductive structures measured in the study. Because only one paper reported this value, we adapted by creating two datasets: one for qualitative analysis that includes any measurement of a reproductive structure, and a second which compares reproductive structures under treatment against controls. These datasets will likely be processed into two papers. One will be an “insight” style paper which describes the current state and research gaps of Cactaceae reproductive studies, and refines opportunities for agro-eco interdisciplinary work. The second will be a formal meta analysis correlating different reproductive structures, investigating allocation theory in Cactaceae.

Based on the data extracted at this point in time, fruit is the most frequently reported reproductive structure (Figure 2). While flowers are the most infrequently reported at this time, an inclusion of “flower*" in a new search will drastically increase this count.

Cactaceae are only native to the Western Hemisphere, excluding one species in Africa (Cota-Sanchez and Bomfim-Patricio 2010). However, members of the family can be found globally thanks to nonnative introductions and agriculture. Of the current studies, most data points are reported in studies occurring in the Western Hemisphere, where they are native (Figure 3). Most reported values and studies occur in field experiments, and field experiments are more likely to report more values per study (Figure 4).

Figure 2: Studies most frequently reported fruit, followed by seed, followed by flower.

Figure 3: Studies on cactus reproduction are more prevalent and report more values in the Western Hemisphere (Figure 3A). Cacti are found globally, but all occurrences in the Eastern Hemisphere are either agricultural or introduced populations (Figure 3B).

Figure 4: More studies take place in the field than in an agricultural plot (Figure 4A), and field studies tend to report more reproductive structure metrics (Figure 4B).

Chapter 2

Linking Avian double mutualistic interactions to successful Cactaceae seed dispersal and facilitation

Purpose: The aim of this study is to determine the strength of this double mutualistic interaction between birds and a foundational species of cactus based on morphological characteristics of cactus individuals.

Research Questions: Are reproductive structures of cacti correlated with each other or with Cylindropuntia acanthocarpa volume? What Avian communities are associated with C. acanthocarpa? How strong are Avian-C. acanthocarpa double mutualistic interactions?

Hypothesis: C. acanthocarpa individuals that maximize size and reproductive output via allocational trade offs will have the showiest reproductive displays, and therefore the most pollinating and seed dispersing Avian visitors.

Predictions: * Flower and fruit production will be positively correlated, but cactus volume and reproductive output will be negatively correlated. * Avian visitation rates and diversity are dependent on cactus morphological characteristics. * Avian diversity at a C. acanthocarpa individual is different than avian diversity at the entire site.

Methods:

Preliminary Cactus Survey Prior to the flowering and fruiting experiments, we performed a transect sampling survey of Cylindropuntia acanthocarpa, Cylindropuntia echinocarpa, and a haphazard sampling of Opuntia basilaris to determine an appropriate study species. We measured the major, minor, and vertical axis of the nearest neighbor cactus every five meters, with distance between transects being five (C. acanthocarpa) or ten (C. echinocarpa) meters. Because C. acanthocarpa was so dense, we were able to sample 105 individuals (n=105) over 5 transects. However, C. echinocarpa was less dense and therefore required 9 transects to be sampled (n=98). O. basilaris was so infrequent that a haphazard search for any individuals was the most effective way to measure the cacti (n=26). We also rated the health of each individual considering the overall percentage of plant death, rot, and scarification. Using this data, we determined that C. acanthocarpa is the most appropriate study species.

Experimental Manipulations Pending the exploratory week, we will return in April/May during the flowering season to observe pollinating birds interactions with 105 cactus individuals (7 replications per characteristic combination). The cacti will have different levels of manipulated “showiness” (0%, 25%, 50%, 75%, 100% percent of flowers) of the 3 size classes. We will snip X% of flowers off the cactus, but also record the number of nonblooming buds on each individual when performing observations, as not all flowers of a cactus bloom concurrently.

While the flowering season for our study cacti is in May, the cactus individual itself only blooms for 1-2 days throughout the season. We will primarily rely on focal observations aided by a 150-600mm lens equipped to a digital camera. We will do 1-hour observations in mornings and evenings at each combination of variables 7 times (105 hours of observations). To avoid impacting bird visitation, we will be at least 10m from the cactus individual and remain still. We will record each bird individual’s species and behavior (using an ethogram). Should there be more than one individual present, we will record the visiting species, but continue behavior observation for the first arrival birds (for up to 10 minutes, although this time limit is unlikely to be surpassed considering bird movement). Once the focal bird has left the cactus of interest, we will note the location it arrived at after leaving the cactus of interest.

We will also leave out omnidirectional microphones to record bird calls, which will give us an estimate of bird diversity site wide. Sound recorders have been shown to be as reliable a measurement of bird presence compared to walking point transects, and are more time and cost effective (Darras et al. 2018). To identify bird calls, we will classify the calls by ear, and then use a audio software program, like Sound Analysis Pro 2011 to identify the many hours of audio data (L. A. Grieves, Logue, and Quinn 2014; Leanne A. Grieves, Logue, and Quinn 2015).

Next, in August, we will begin the fruiting observation and experiment–it will be nearly identical to the flowering experiment, but with some added components. Each combination of variables (species, size, and fruit percent) will again have 7 replicates, meaning 105 cacti will be a part of the study. We will remove 0%, 25%, 50%, 75%, and 100% of fruits from small, medium, and large cacti. We will immediately place each cactus’s fruit in a sealed zip lock bag to prevent desiccation while in the field. Post collection, we will weigh fresh and dried fruits, and sieve the seeds for weighing and counting. For the fruiting season, all focal observation protocols will be identical to the flowering season’s, but replacing flowers for fruit.

Joy Sampling Methodology In addition to our manipulated experiments, we will also perform joy sampling protocols, which differ in that no cacti will be altered. First, we will perform 50 hours worth of area searches (2 hours per session), recording any and all bird locations, behaviors, and mesohabitats (shrub, cactus, open, etc.) Conversely, we will perform 50 hours worth of point counts at individual cacti. This protocol is easily replicable at other sites with different collaborators.

Preliminary Results:

Abundance, size, and health are three factors under consideration when choosing a study species. C. acanthocarpa was dominant, C. echinocarpa was second most common, and O. basilaris was infrequent (Figure 5). Based on our proposed methods, a total of 210 distinct individuals will be manipulated for observation, as well as an additional 100 for point count observations, and 20 for flower-fruit paired observations (n=360), so an abundant species is necessary.

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Figure 5: C. acanthocarpa is the most abundant cactus species, C. echinocarpa is the second most common, and O. basilaris is infrequent. Figure 5a shows all cacti measured, figure 5b zooms in on C. acanthocarpa area.

In addition to abundance, we need to know if the sizes are variable enough to split into three size classes (small, medium, and large). While we do have a total volume available, height of cacti is a better metric to consider if nectarivorous and frugivorous birds will engage with a cactus, as they prefer to engage with higher inflorescence and fruits (Wolf and Hainsworth 1990; Mitchell 1994). Sampled O. basilaris size was normally distributed (Shapiro Wilks, p = 0.008519, W = 0.88797), but C. acanthocarpa (Shapiro Wilks, p = 0.06667, W = 0.97717) and C. echinocarpa (Shapiro Wilks, p = 0.349, W = 0.98532) were not. A Kruskall Wallis rank sum test revealed that each cactus had non-identical means (Kruskal-Wallis, Chi-square = 3.71, p > 0.0001, df = 52), with a mean height in meters of 1.04 meters for C. acanthocarpa, 0.55 meters for C. echinocarpa, and 0.17 meters for O. basilaris (Figure 6). Additionally, the selected study species must have enough variety in heights so as to be binned into three size class (small, medium, large). Based on the distributions of sizes of each cactus, a equal-sized binned class system is most appropriate. C. acanthocarpa has the largest bin classes, which is a benefit in that having large size classes translates to a clearer distinction among flower/fruit height for birds.

Figure 6: Each cactus species had significantly different mean heights (Kruskal-Wallis, Chi-square = 3.71, p > 0.0001, df = 52).

species small medium large
Cylindropuntia acanthocarpa <85cm 86cm - 152cm >153cm
Cylindropuntia enchinocarpa <45cm 46cm - 72cm >73cm
Opuntia basilaris <15cm 16cm - 22cm >23cm

Table 3: Size classes for each study species candidate. C. acanthocarpa has the largest bin sizes.

Overall health is another important factor to consider when exploring potential study species, as health can determine an individual’s likelihood to flower and fruit. C. acanthocarpa and C. echinocarpa are left skewed, with most individuals having health ratings of “4” or “5”, whereas O. basilaris has an even distribution of health classes among all individuals (Figure 7).

Figure 7: The Cylindropuntia species tend to have more individuals with “4” or “5” health index ratings, whereas the O. basilaris individuals are evenly distributed along the health index scale.

Considering the abundance, the density, the health, and size class options, O. basilaris is not a realistic contender as a study species. It may be overlooked by birds, not bloom/fruit due to health, and is in short supply. Both of Cylindropuntias are healthy. C. echinocarpa, however, is still less dominant than C. acanthocarpa, is smaller overall, and doesn’t have the width of size classes that C. acanthocarpa does. While these traits do not mean the C. echinocarpa could not be viable study species, I propose that focusing more deeply on C. acanthocarpa and deepening the methods of observation will be more beneficial to answering my study questions than a comparative study between cacti species would.

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